JPH0459049A - Catalyst for diesel engine exhaust gas cleanup - Google Patents
Catalyst for diesel engine exhaust gas cleanupInfo
- Publication number
- JPH0459049A JPH0459049A JP2159922A JP15992290A JPH0459049A JP H0459049 A JPH0459049 A JP H0459049A JP 2159922 A JP2159922 A JP 2159922A JP 15992290 A JP15992290 A JP 15992290A JP H0459049 A JPH0459049 A JP H0459049A
- Authority
- JP
- Japan
- Prior art keywords
- catalyst
- rhodium
- alumina
- palladium
- exhaust gas
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 239000003054 catalyst Substances 0.000 title claims abstract description 120
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 claims abstract description 80
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 claims abstract description 79
- 239000010948 rhodium Substances 0.000 claims abstract description 65
- 229910052703 rhodium Inorganic materials 0.000 claims abstract description 64
- MHOVAHRLVXNVSD-UHFFFAOYSA-N rhodium atom Chemical compound [Rh] MHOVAHRLVXNVSD-UHFFFAOYSA-N 0.000 claims abstract description 63
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims abstract description 39
- 229910052763 palladium Inorganic materials 0.000 claims abstract description 39
- 229910052697 platinum Inorganic materials 0.000 claims abstract description 39
- 229910052809 inorganic oxide Inorganic materials 0.000 claims abstract description 14
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims abstract description 12
- 239000000919 ceramic Substances 0.000 claims abstract description 12
- 239000000377 silicon dioxide Substances 0.000 claims abstract description 6
- 239000006260 foam Substances 0.000 claims abstract description 5
- 229910000510 noble metal Inorganic materials 0.000 claims abstract description 5
- MCMNRKCIXSYSNV-UHFFFAOYSA-N Zirconium dioxide Chemical compound O=[Zr]=O MCMNRKCIXSYSNV-UHFFFAOYSA-N 0.000 claims description 30
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 claims description 12
- 229910052751 metal Inorganic materials 0.000 claims description 7
- 239000002184 metal Substances 0.000 claims description 7
- 238000000746 purification Methods 0.000 claims description 6
- 239000006262 metallic foam Substances 0.000 claims description 3
- 229910021536 Zeolite Inorganic materials 0.000 claims description 2
- 230000003197 catalytic effect Effects 0.000 claims description 2
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims description 2
- 230000009970 fire resistant effect Effects 0.000 claims description 2
- 239000010457 zeolite Substances 0.000 claims description 2
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 abstract description 14
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 abstract description 5
- 229910002091 carbon monoxide Inorganic materials 0.000 abstract description 2
- 230000001590 oxidative effect Effects 0.000 abstract description 2
- 150000003283 rhodium Chemical class 0.000 abstract description 2
- 239000000126 substance Substances 0.000 abstract description 2
- 239000002002 slurry Substances 0.000 description 58
- 239000000843 powder Substances 0.000 description 35
- 239000007864 aqueous solution Substances 0.000 description 24
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 23
- 239000008367 deionised water Substances 0.000 description 22
- 229910021641 deionized water Inorganic materials 0.000 description 22
- 241000264877 Hippospongia communis Species 0.000 description 17
- 239000013618 particulate matter Substances 0.000 description 16
- 230000000052 comparative effect Effects 0.000 description 13
- 239000000203 mixture Substances 0.000 description 11
- VXNYVYJABGOSBX-UHFFFAOYSA-N rhodium(3+);trinitrate Chemical compound [Rh+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O VXNYVYJABGOSBX-UHFFFAOYSA-N 0.000 description 11
- 229910052799 carbon Inorganic materials 0.000 description 9
- GPNDARIEYHPYAY-UHFFFAOYSA-N palladium(ii) nitrate Chemical compound [Pd+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O GPNDARIEYHPYAY-UHFFFAOYSA-N 0.000 description 9
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 8
- 229930195733 hydrocarbon Natural products 0.000 description 7
- 150000002430 hydrocarbons Chemical class 0.000 description 7
- AKEJUJNQAAGONA-UHFFFAOYSA-N sulfur trioxide Chemical compound O=S(=O)=O AKEJUJNQAAGONA-UHFFFAOYSA-N 0.000 description 7
- 238000003756 stirring Methods 0.000 description 6
- 239000002253 acid Substances 0.000 description 5
- 229910052878 cordierite Inorganic materials 0.000 description 5
- JSKIRARMQDRGJZ-UHFFFAOYSA-N dimagnesium dioxido-bis[(1-oxido-3-oxo-2,4,6,8,9-pentaoxa-1,3-disila-5,7-dialuminabicyclo[3.3.1]nonan-7-yl)oxy]silane Chemical compound [Mg++].[Mg++].[O-][Si]([O-])(O[Al]1O[Al]2O[Si](=O)O[Si]([O-])(O1)O2)O[Al]1O[Al]2O[Si](=O)O[Si]([O-])(O1)O2 JSKIRARMQDRGJZ-UHFFFAOYSA-N 0.000 description 5
- FCUFAHVIZMPWGD-UHFFFAOYSA-N [O-][N+](=O)[Pt](N)(N)[N+]([O-])=O Chemical compound [O-][N+](=O)[Pt](N)(N)[N+]([O-])=O FCUFAHVIZMPWGD-UHFFFAOYSA-N 0.000 description 4
- 229910002090 carbon oxide Inorganic materials 0.000 description 4
- 239000010419 fine particle Substances 0.000 description 4
- MRELNEQAGSRDBK-UHFFFAOYSA-N lanthanum oxide Inorganic materials [O-2].[O-2].[O-2].[La+3].[La+3] MRELNEQAGSRDBK-UHFFFAOYSA-N 0.000 description 4
- 238000000034 method Methods 0.000 description 4
- PIBWKRNGBLPSSY-UHFFFAOYSA-L palladium(II) chloride Chemical compound Cl[Pd]Cl PIBWKRNGBLPSSY-UHFFFAOYSA-L 0.000 description 4
- 239000002245 particle Substances 0.000 description 4
- 229910003447 praseodymium oxide Inorganic materials 0.000 description 4
- 150000003839 salts Chemical class 0.000 description 4
- 239000000243 solution Substances 0.000 description 4
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 3
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 3
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 3
- 238000002485 combustion reaction Methods 0.000 description 3
- 238000010304 firing Methods 0.000 description 3
- 239000000446 fuel Substances 0.000 description 3
- 239000007858 starting material Substances 0.000 description 3
- 239000011593 sulfur Substances 0.000 description 3
- 229910052717 sulfur Inorganic materials 0.000 description 3
- 244000000626 Daucus carota Species 0.000 description 2
- 235000002767 Daucus carota Nutrition 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- 229910052783 alkali metal Inorganic materials 0.000 description 2
- 150000001340 alkali metals Chemical class 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- CETPSERCERDGAM-UHFFFAOYSA-N ceric oxide Chemical compound O=[Ce]=O CETPSERCERDGAM-UHFFFAOYSA-N 0.000 description 2
- HSJPMRKMPBAUAU-UHFFFAOYSA-N cerium(3+);trinitrate Chemical compound [Ce+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O HSJPMRKMPBAUAU-UHFFFAOYSA-N 0.000 description 2
- 229910000422 cerium(IV) oxide Inorganic materials 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 229910052746 lanthanum Inorganic materials 0.000 description 2
- FZLIPJUXYLNCLC-UHFFFAOYSA-N lanthanum atom Chemical compound [La] FZLIPJUXYLNCLC-UHFFFAOYSA-N 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 230000003647 oxidation Effects 0.000 description 2
- 238000007254 oxidation reaction Methods 0.000 description 2
- MMKQUGHLEMYQSG-UHFFFAOYSA-N oxygen(2-);praseodymium(3+) Chemical compound [O-2].[O-2].[O-2].[Pr+3].[Pr+3] MMKQUGHLEMYQSG-UHFFFAOYSA-N 0.000 description 2
- 150000002941 palladium compounds Chemical class 0.000 description 2
- JRTYPQGPARWINR-UHFFFAOYSA-N palladium platinum Chemical compound [Pd].[Pt] JRTYPQGPARWINR-UHFFFAOYSA-N 0.000 description 2
- AAIMUHANAAXZIF-UHFFFAOYSA-L platinum(2+);sulfite Chemical compound [Pt+2].[O-]S([O-])=O AAIMUHANAAXZIF-UHFFFAOYSA-L 0.000 description 2
- 229910052761 rare earth metal Inorganic materials 0.000 description 2
- 150000003284 rhodium compounds Chemical class 0.000 description 2
- SONJTKJMTWTJCT-UHFFFAOYSA-K rhodium(iii) chloride Chemical compound [Cl-].[Cl-].[Cl-].[Rh+3] SONJTKJMTWTJCT-UHFFFAOYSA-K 0.000 description 2
- 238000002791 soaking Methods 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 239000010935 stainless steel Substances 0.000 description 2
- 229910001220 stainless steel Inorganic materials 0.000 description 2
- 150000003467 sulfuric acid derivatives Chemical class 0.000 description 2
- HMUNWXXNJPVALC-UHFFFAOYSA-N 1-[4-[2-(2,3-dihydro-1H-inden-2-ylamino)pyrimidin-5-yl]piperazin-1-yl]-2-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)ethanone Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)N1CCN(CC1)C(CN1CC2=C(CC1)NN=N2)=O HMUNWXXNJPVALC-UHFFFAOYSA-N 0.000 description 1
- VZSRBBMJRBPUNF-UHFFFAOYSA-N 2-(2,3-dihydro-1H-inden-2-ylamino)-N-[3-oxo-3-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)propyl]pyrimidine-5-carboxamide Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)C(=O)NCCC(N1CC2=C(CC1)NN=N2)=O VZSRBBMJRBPUNF-UHFFFAOYSA-N 0.000 description 1
- SXAMGRAIZSSWIH-UHFFFAOYSA-N 2-[3-[2-(2,3-dihydro-1H-inden-2-ylamino)pyrimidin-5-yl]-1,2,4-oxadiazol-5-yl]-1-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)ethanone Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)C1=NOC(=N1)CC(=O)N1CC2=C(CC1)NN=N2 SXAMGRAIZSSWIH-UHFFFAOYSA-N 0.000 description 1
- ZRPAUEVGEGEPFQ-UHFFFAOYSA-N 2-[4-[2-(2,3-dihydro-1H-inden-2-ylamino)pyrimidin-5-yl]pyrazol-1-yl]-1-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)ethanone Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)C=1C=NN(C=1)CC(=O)N1CC2=C(CC1)NN=N2 ZRPAUEVGEGEPFQ-UHFFFAOYSA-N 0.000 description 1
- YJLUBHOZZTYQIP-UHFFFAOYSA-N 2-[5-[2-(2,3-dihydro-1H-inden-2-ylamino)pyrimidin-5-yl]-1,3,4-oxadiazol-2-yl]-1-(2,4,6,7-tetrahydrotriazolo[4,5-c]pyridin-5-yl)ethanone Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)C1=NN=C(O1)CC(=O)N1CC2=C(CC1)NN=N2 YJLUBHOZZTYQIP-UHFFFAOYSA-N 0.000 description 1
- CONKBQPVFMXDOV-QHCPKHFHSA-N 6-[(5S)-5-[[4-[2-(2,3-dihydro-1H-inden-2-ylamino)pyrimidin-5-yl]piperazin-1-yl]methyl]-2-oxo-1,3-oxazolidin-3-yl]-3H-1,3-benzoxazol-2-one Chemical compound C1C(CC2=CC=CC=C12)NC1=NC=C(C=N1)N1CCN(CC1)C[C@H]1CN(C(O1)=O)C1=CC2=C(NC(O2)=O)C=C1 CONKBQPVFMXDOV-QHCPKHFHSA-N 0.000 description 1
- 239000004215 Carbon black (E152) Substances 0.000 description 1
- 229910052684 Cerium Inorganic materials 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- ZOKXTWBITQBERF-UHFFFAOYSA-N Molybdenum Chemical compound [Mo] ZOKXTWBITQBERF-UHFFFAOYSA-N 0.000 description 1
- OKIZCWYLBDKLSU-UHFFFAOYSA-M N,N,N-Trimethylmethanaminium chloride Chemical compound [Cl-].C[N+](C)(C)C OKIZCWYLBDKLSU-UHFFFAOYSA-M 0.000 description 1
- 229910052779 Neodymium Inorganic materials 0.000 description 1
- 229910052777 Praseodymium Inorganic materials 0.000 description 1
- 229910001260 Pt alloy Inorganic materials 0.000 description 1
- 241000220317 Rosa Species 0.000 description 1
- BLRPTPMANUNPDV-UHFFFAOYSA-N Silane Chemical group [SiH4] BLRPTPMANUNPDV-UHFFFAOYSA-N 0.000 description 1
- 241000212342 Sium Species 0.000 description 1
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 description 1
- 244000269722 Thea sinensis Species 0.000 description 1
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 1
- LBHVUTSICSHCFE-UHFFFAOYSA-N [O-][N+](=O)N([Pt])[N+]([O-])=O Chemical compound [O-][N+](=O)N([Pt])[N+]([O-])=O LBHVUTSICSHCFE-UHFFFAOYSA-N 0.000 description 1
- 239000004480 active ingredient Substances 0.000 description 1
- 229910052784 alkaline earth metal Inorganic materials 0.000 description 1
- 150000001342 alkaline earth metals Chemical class 0.000 description 1
- 229910045601 alloy Inorganic materials 0.000 description 1
- 239000000956 alloy Substances 0.000 description 1
- 239000002585 base Substances 0.000 description 1
- 230000033228 biological regulation Effects 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- ZMIGMASIKSOYAM-UHFFFAOYSA-N cerium Chemical compound [Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce] ZMIGMASIKSOYAM-UHFFFAOYSA-N 0.000 description 1
- 229910000420 cerium oxide Inorganic materials 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 239000010949 copper Substances 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 238000004453 electron probe microanalysis Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 230000005183 environmental health Effects 0.000 description 1
- PCHJSUWPFVWCPO-UHFFFAOYSA-N gold Chemical compound [Au] PCHJSUWPFVWCPO-UHFFFAOYSA-N 0.000 description 1
- 229910052737 gold Inorganic materials 0.000 description 1
- 239000010931 gold Substances 0.000 description 1
- 229910021505 gold(III) hydroxide Inorganic materials 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 235000012907 honey Nutrition 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- FYDKNKUEBJQCCN-UHFFFAOYSA-N lanthanum(3+);trinitrate Chemical compound [La+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O FYDKNKUEBJQCCN-UHFFFAOYSA-N 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229910052750 molybdenum Inorganic materials 0.000 description 1
- 239000011733 molybdenum Substances 0.000 description 1
- QEFYFXOXNSNQGX-UHFFFAOYSA-N neodymium atom Chemical compound [Nd] QEFYFXOXNSNQGX-UHFFFAOYSA-N 0.000 description 1
- 239000003960 organic solvent Substances 0.000 description 1
- BMMGVYCKOGBVEV-UHFFFAOYSA-N oxo(oxoceriooxy)cerium Chemical compound [Ce]=O.O=[Ce]=O BMMGVYCKOGBVEV-UHFFFAOYSA-N 0.000 description 1
- BPUBBGLMJRNUCC-UHFFFAOYSA-N oxygen(2-);tantalum(5+) Chemical compound [O-2].[O-2].[O-2].[O-2].[O-2].[Ta+5].[Ta+5] BPUBBGLMJRNUCC-UHFFFAOYSA-N 0.000 description 1
- 229910003445 palladium oxide Inorganic materials 0.000 description 1
- KZICDIJTWVWHCV-UHFFFAOYSA-N palladium praseodymium Chemical compound [Pd].[Pd].[Pd].[Pd].[Pd].[Pr] KZICDIJTWVWHCV-UHFFFAOYSA-N 0.000 description 1
- -1 palladium sulfite salt Chemical class 0.000 description 1
- 229920000642 polymer Polymers 0.000 description 1
- PUDIUYLPXJFUGB-UHFFFAOYSA-N praseodymium atom Chemical compound [Pr] PUDIUYLPXJFUGB-UHFFFAOYSA-N 0.000 description 1
- YWECOPREQNXXBZ-UHFFFAOYSA-N praseodymium(3+);trinitrate Chemical compound [Pr+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O YWECOPREQNXXBZ-UHFFFAOYSA-N 0.000 description 1
- 239000010970 precious metal Substances 0.000 description 1
- 229910052705 radium Inorganic materials 0.000 description 1
- HCWPIIXVSYCSAN-UHFFFAOYSA-N radium atom Chemical compound [Ra] HCWPIIXVSYCSAN-UHFFFAOYSA-N 0.000 description 1
- 230000029058 respiratory gaseous exchange Effects 0.000 description 1
- 229910003450 rhodium oxide Inorganic materials 0.000 description 1
- LUPXXYYDGLTVDU-UHFFFAOYSA-K rhodium(3+) trichlorite Chemical compound [Rh+3].[O-][Cl]=O.[O-][Cl]=O.[O-][Cl]=O LUPXXYYDGLTVDU-UHFFFAOYSA-K 0.000 description 1
- 239000000523 sample Substances 0.000 description 1
- 229910001936 tantalum oxide Inorganic materials 0.000 description 1
- XQQWBPOEMYKKBY-UHFFFAOYSA-H trimagnesium;dicarbonate;dihydroxide Chemical compound [OH-].[OH-].[Mg+2].[Mg+2].[Mg+2].[O-]C([O-])=O.[O-]C([O-])=O XQQWBPOEMYKKBY-UHFFFAOYSA-H 0.000 description 1
- 229910052720 vanadium Inorganic materials 0.000 description 1
- GPPXJZIENCGNKB-UHFFFAOYSA-N vanadium Chemical compound [V]#[V] GPPXJZIENCGNKB-UHFFFAOYSA-N 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9445—Simultaneously removing carbon monoxide, hydrocarbons or nitrogen oxides making use of three-way catalysts [TWC] or four-way-catalysts [FWC]
- B01D53/945—Simultaneously removing carbon monoxide, hydrocarbons or nitrogen oxides making use of three-way catalysts [TWC] or four-way-catalysts [FWC] characterised by a specific catalyst
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/38—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
- B01J23/54—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
- B01J23/56—Platinum group metals
- B01J23/58—Platinum group metals with alkali- or alkaline earth metals
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/944—Simultaneously removing carbon monoxide, hydrocarbons or carbon making use of oxidation catalysts
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/38—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
- B01J23/40—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals of the platinum group metals
- B01J23/46—Ruthenium, rhodium, osmium or iridium
- B01J23/464—Rhodium
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
- B01J37/02—Impregnation, coating or precipitation
- B01J37/024—Multiple impregnation or coating
- B01J37/0244—Coatings comprising several layers
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F02—COMBUSTION ENGINES; HOT-GAS OR COMBUSTION-PRODUCT ENGINE PLANTS
- F02B—INTERNAL-COMBUSTION PISTON ENGINES; COMBUSTION ENGINES IN GENERAL
- F02B3/00—Engines characterised by air compression and subsequent fuel addition
- F02B3/06—Engines characterised by air compression and subsequent fuel addition with compression ignition
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
-
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Abstract
Description
【発明の詳細な説明】
(産業上の利用分野)
本発明は、ディーゼルエンジン排ガス浄化用触媒に関す
る。DETAILED DESCRIPTION OF THE INVENTION (Field of Industrial Application) The present invention relates to a catalyst for purifying diesel engine exhaust gas.
(従来の技術)
近年、特にディーゼルエンジン排ガス中の微粒子物質で
主として、固体状炭素微粒子、硫酸塩などの硫黄系微粒
子、液状ないし固体状の高分子炭化水素微粒子などから
なるものであり、以下、これらを「微粒子物質」と総称
する)か環境衛生」二問題となっている。その理由は、
これら微粒子物質は、その粒子径がほとんと1ミクロン
以下であるため、大気中に浮遊しやすく呼吸により人体
内に取り込まれやすいためである。従って、これら微粒
子物質のディーゼルエンジンからの排出に関する規制を
厳しくしていく方向で検討が進められている。(Prior Art) In recent years, particulate matter particularly in diesel engine exhaust gas mainly consists of solid carbon particles, sulfur-based particles such as sulfates, liquid or solid polymer hydrocarbon particles, etc. These are collectively referred to as ``fine particulate matter'') and environmental health. The reason is,
This is because these particulate substances have particle diameters of approximately 1 micron or less, and therefore are easily suspended in the atmosphere and easily taken into the human body through breathing. Therefore, studies are underway to tighten regulations regarding the emission of these particulate matter from diesel engines.
一方、ディーゼルエンジンの燃利噴羽の高圧化、燃利噴
羽タイミンクの制御なとの改良にともない、ディーゼル
エンジンから排出される微粒子物質の量はある程度低減
された。しかし、その低減化は来た十分とはいえず、ま
た微粒子物質に含まれる、主として液状の高分子量炭化
水素からなる有機溶媒tこ可溶な成分(S OF)は、
」二記のようなエンジンの改良によって(よ除去できず
、微粒子物質中のSOF割合は増加する結果となってい
る。このSOFは発カン性物質なとの有害成分な舎イ1
することから、微粒子物質とともにSOFの除去が重要
な問題となっている。On the other hand, improvements such as increasing the pressure of the fuel jets of diesel engines and controlling the timing of the fuel jets have reduced the amount of particulate matter emitted from diesel engines to some extent. However, the reduction has not been sufficient, and organic solvent soluble components (SOF), which mainly consist of liquid high molecular weight hydrocarbons, are contained in particulate matter.
Improvements in engines such as those described in Section 2 have resulted in an increase in the proportion of SOF in particulate matter.
Therefore, removal of SOF along with particulate matter has become an important issue.
微粒子物質の除去方法としては、セラミックフオーム、
ワイヤーメツシュ、金属発泡体、目利しタイプのセラミ
ックハニカム、オープンフロータイブのセラミックハニ
カム、メタルハニカムなとの附火性三次元構造体に炭素
系微粒子を燃焼させうる触媒物質な担持させた触媒を使
用し、ディーゼルエンジン排ガス中の微粒子物質を捕捉
するとともに、通常のデイ−セルエンジンの走行条件下
て得られる排ガスの排出条件(ガス組成および温度)下
に、あるいは電気ヒーターなとの加熱手段を用いて炭素
系微粒子を除去する触媒方式が検3Jされている。Ceramic foam,
Catalysts supported on combustible three-dimensional structures such as wire mesh, metal foam, graded ceramic honeycombs, open flow type ceramic honeycombs, and metal honeycombs, which are capable of burning carbon-based fine particles. is used to capture particulate matter in the diesel engine exhaust gas, and under the exhaust gas emission conditions (gas composition and temperature) obtained under normal day-cell engine running conditions, or by means of heating such as an electric heater. A catalytic method for removing carbon-based particulates using carbon dioxide has been investigated.
一般に、デイ−セルエンジンの排ガス浄化用触媒として
は、 (イ)炭素系微粒子のほか未燃焼炭化水素、−酸
化炭素などの有害成分の低温からの燃焼除去効率か高い
、 ([ニア)燃トドとして用いる軽油中に多量に含ま
れる硫黄成分から発生ずる二酸(ヒ硫黄C3O2)の三
酸化硫黄(SO3)への酸化能が低く、ザルフエ−1・
(二酸化硫黄が酸化されて三酸化硫黄や硫酸ミスI・に
なったもの)の生成を抑制できる、また(ハ)高負荷で
の連続運転下でも耐える、いわゆる高温耐久性が高いと
いう性能を有する触媒が望まれている。In general, catalysts for purifying exhaust gas from day-cell engines have the following characteristics: (a) high efficiency in combustion removal of harmful components such as carbon-based particulates, unburned hydrocarbons, and carbon oxides from low temperatures; It has a low ability to oxidize diacid (Hisulfur C3O2), which is generated from the sulfur component contained in a large amount in light oil used as a gas oil, to sulfur trioxide (SO3).
(3) It has the ability to suppress the formation of sulfur dioxide (oxidized to sulfur trioxide and sulfuric acid), and (3) it has the ability to withstand continuous operation under high loads, so-called high temperature durability. Catalysts are desired.
従来より、炭素系微粒子の燃焼除去効率を高める目的で
種々の提案かなされている。Conventionally, various proposals have been made for the purpose of increasing the combustion removal efficiency of carbon-based particulates.
例えは、特開昭55−24!397号公報には、白金族
元素系触媒として、ロジウム(7,5%)白金合金、白
金/パラジウム(50/ 50 )混合物、酸化タンタ
ルまたは酸化セリウム」−にパラジウムを担持したもの
、さらにはパラジウムと75重量%以下の白金とからな
る合金などが開示されている。これら触媒はまたSOF
の除去にも効果的であるとされている。For example, JP-A-55-24!397 discloses that platinum group element catalysts include rhodium (7.5%) platinum alloy, platinum/palladium (50/50) mixture, tantalum oxide, or cerium oxide. Also disclosed are alloys containing palladium and 75% by weight or less of platinum. These catalysts are also SOF
It is also said to be effective in removing.
その他、特開昭61−129030号、同61−14.
9222号および同61−146314号各公報には、
パラジウムとロジウムとを主な活性成分とし、ざらにア
ルカリ金属、アルカリ土類金属、銅、ランタン、亜鉛お
よびマンカンなどを添加した触媒組成物が、また特開昭
59−82944号公報には、銅、アルカリ金属、モリ
ブデンおよびバナジウムから選ばれる少なくとも1種と
白金、ロジウムおよびパラジウムから選ばれる少なくと
も1種とを矧み合わぜた触媒組成物が開示されている。In addition, JP-A-61-129030, JP-A No. 61-14.
9222 and 61-146314,
A catalyst composition containing palladium and rhodium as the main active ingredients, with the addition of alkali metals, alkaline earth metals, copper, lanthanum, zinc, mankan, etc. is also disclosed in JP-A-59-82944. , alkali metals, molybdenum, and vanadium and at least one selected from platinum, rhodium, and palladium are disclosed.
ざらごこ、ディーゼルエンジン排ガス中のSOFを除去
する触媒として、ガス流れに対し平行に貫通孔を有する
オーブン式のハニカム状貴金属系酸化触媒が報告されて
いる(SA、E Paper、810263)。An oven-type honeycomb-shaped noble metal oxidation catalyst having through holes parallel to the gas flow has been reported as a catalyst for removing SOF from diesel engine exhaust gas (SA, E Paper, 810263).
(発明か解決しようとする課題)
しかし、上記従来の触媒は、いずれも萩素系微粒子の燃
焼除去またはSOFの除去にはある程度効果的であるが
、二酸化硫黄の酸化能が高いため、→ノルフェートの生
成量が増加し、かえって微粒子物質全体の除去率は低下
し、またこのサルフェートが新たな環境問題を生しると
いう欠点かあった。(Problem to be solved by the invention) However, although the above-mentioned conventional catalysts are all effective to some extent in the combustion removal of Hagi-based fine particles or the removal of SOF, they have a high ability to oxidize sulfur dioxide. The production amount of sulfate increases, and the overall removal rate of particulate matter decreases, and this sulfate also poses a new environmental problem.
すなわち、前記した(イ)〜(ハ)のディーゼルニンジ
ン排ガス浄化用の触媒に要求される性能、ざらにSOF
の除去性能を十分倫えた触媒?i来た見出されていない
。In other words, the performance required for the catalyst for purifying diesel carrot exhaust gas in (a) to (c) above, roughly speaking, the SOF
A catalyst with sufficient removal performance? i have not been found.
従って、本発明の一つの目的は、ディーゼルニンジン排
ガス中の微粒子物質を効率よく除去できるディーゼルエ
ンジン11ガス浄化用触媒を提供することである。Therefore, one object of the present invention is to provide a catalyst for purifying diesel engine 11 gas that can efficiently remove particulate matter from diesel carrot exhaust gas.
本発明の他の目的は、ディーゼルエンジン排ガス中の炭
素系微粒子のほか未燃焼炭化水素、−酸化炭素なとの有
害成分も低温から燃焼除去できる性能を有し、しかも二
酸化硫黄の酸化能が低くサルフェートの生成を抑制した
ディーゼルエンジン浄化用触媒を提供することである。Another object of the present invention is to have the ability to burn off harmful components such as unburned hydrocarbons and carbon oxides in addition to carbon-based particulates in diesel engine exhaust gas at low temperatures, and to have a low oxidizing ability for sulfur dioxide. An object of the present invention is to provide a catalyst for purifying a diesel engine that suppresses the generation of sulfate.
本発明の他の目的は、ディーゼルエンジン排ガス中のS
OFを効率よく除去できるデイーセルコーンシン排ガス
浄化用触媒を提供することである。Another object of the present invention is to reduce the amount of S in diesel engine exhaust gas.
An object of the present invention is to provide a catalyst for purifying diesel exhaust gas that can efficiently remove OF.
本発明の他の目的は、高温耐久性か良好てあフた、実用
」二問題を生しることなくディーゼル車に搭載できるデ
イ−セルエンジン浄化用触媒を提供することである。Another object of the present invention is to provide a day-cell engine purifying catalyst that can be installed in a diesel vehicle without causing problems such as high temperature durability, good after-effects, and practical use.
(課題を解決するための手段)
本発明者らは、」二記目的を達成するために鋭意検L」
シた結果、 (a ) 1rtiJ火性無機酸化物、
(1))パラジウムおよび/または白金、ならびに(c
)ロジウムを含有する触媒成分を耐火性三次元構造体に
担持した触媒であって、ロジウムを触媒成分担持層の上
層部に選択的に含有する触媒か炭素系微粒子のほか未燃
焼炭化水素、−酸化炭素なとの有害成分を低温から燃焼
除去する性能に優れ、また二酸化硫黄の酸化能か低く、
さらにはSOFの除去にも効果的であることを知り、こ
の知見に基ついて本発明を完成するに至った。(Means for Solving the Problems) The inventors have made extensive efforts to achieve the objects stated in section 2.
As a result, (a) 1rtiJ flammable inorganic oxide,
(1)) palladium and/or platinum, and (c
) A catalyst in which a catalyst component containing rhodium is supported on a refractory three-dimensional structure, which selectively contains rhodium in the upper layer of the catalyst component support layer, or in addition to carbon-based fine particles, unburned hydrocarbons, - It has excellent performance in burning and removing harmful components such as carbon oxide at low temperatures, and has a low ability to oxidize sulfur dioxide.
Furthermore, they found that it is effective in removing SOF, and based on this knowledge, they completed the present invention.
すなわち、本発明は、 (a)耐火性無N酸化物、(l
〕)パラジウムおよび白金から選ばれる少なくとも1種
の貴金属、ならびに(c)ロジウムを含有する触媒成分
を耐火性三次元構造体に担持したディーゼルエンジン排
ガス浄化用触媒であって、触媒成分担持層の厚さの80
%以下に相当する厚さの上層部分のみにロジウムか含有
されていることを特徴とするディーゼルエンジン排ガス
浄化用触媒に関する。That is, the present invention provides (a) a refractory N-free oxide, (l
]) A catalyst for diesel engine exhaust gas purification in which a fire-resistant three-dimensional structure supports a catalyst component containing at least one noble metal selected from palladium and platinum, and (c) rhodium, the catalyst component supporting layer having a thickness of Sano 80
The present invention relates to a catalyst for purifying diesel engine exhaust gas, characterized in that rhodium is contained only in the upper layer portion with a thickness corresponding to % or less.
以下、本発明の詳細な説明する。The present invention will be explained in detail below.
耐火性無機酸化物(a)としては、活性アルミナ、シリ
カ、チタニア、ジルコニア、シリカ−アルミナ、アルミ
ナ−ジルコニア、アルミナ−チタニア、シリカ−チタニ
ア、シリカ−ジルコニア、チタニア−ジルコニア、ゼオ
ライトなどが用いられる。これらのうぢ、ジルコニアか
サルフェ−トの生成を抑制し、優れた選択酸化能を発現
する好適な基材として挙げることかできる。As the refractory inorganic oxide (a), activated alumina, silica, titania, zirconia, silica-alumina, alumina-zirconia, alumina-titania, silica-titania, silica-zirconia, titania-zirconia, zeolite, etc. are used. Zirconia can be cited as a suitable base material that suppresses the formation of sulfate and exhibits excellent selective oxidation ability.
成分(b)の−っである白金の出発原料としては、塩化
白金酸、ジニトロジアミノ白金、白金テトラミンクロラ
イド、白金スルフィト錯塩などを掌げることかできる。As the starting material for platinum, which is component (b), chloroplatinic acid, dinitrodiaminoplatinum, platinum tetramine chloride, platinum sulfite complex salts, etc. can be used.
また、パラジウムの出発原料としては、硝酸パラジウム
、塩化パラジウム、バラシラノ、テトラミンクIJライ
ト、パラジウムスルフィト銘塩なとを挙りることかてき
る。In addition, starting materials for palladium include palladium nitrate, palladium chloride, balacillano, tetramink IJ light, and palladium sulfite salt.
成分(c)としてのロジウムの出発原料としては、硝酸
ロジウム、J\キサアンミンロジウムクロライド、ロジ
ウムスルフィI−錯塩なとを挙げることかできる。Examples of the starting material for rhodium as component (c) include rhodium nitrate, J\xaammine rhodium chloride, and rhodium sulfi I-complex salt.
また、耐火性三次元構造体としては、セラミックフオー
ム、オーブラフ1コーのセラミックハニカム、ウォール
フロータイプのハニカムモノリス、オープンフローのメ
タルハニカム、金属発泡体またはメタルメツシュなどを
用いることかできる。Further, as the refractory three-dimensional structure, ceramic foam, ceramic honeycomb of one orb rough type, wall flow type honeycomb monolith, open flow metal honeycomb, metal foam, metal mesh, etc. can be used.
特に、ディーゼルエンジン排ガスが排ガス1工η3あた
り100mg以下の微粒子物質を含み、またこの微粒子
物質中のSOF含有率が20%以上である場合、面・]
火性三次元υ4造体としてはオープンフロータイブのセ
ラミックハニカムJ:たはメタルハニカムか好適に使用
される。In particular, if the diesel engine exhaust gas contains 100 mg or less of particulate matter per 1 hour of exhaust gas, and the SOF content in this particulate matter is 20% or more,
As the flammable three-dimensional υ4 structure, open flow type ceramic honeycomb or metal honeycomb is suitably used.
本発明の触媒は、上記耐火性三次元構造体に」―記成分
(a)〜(c)を含有する触媒成分を担持したものであ
り、触媒成分担持層の厚さの80%以下(なお、ロジウ
ムか存在しないことになる0%は除外される)に相当す
る厚さの]−層部分のみにロジウムか含有されているこ
とを特徴とするものである。すなわち、本発明の触媒に
おいては、ロジウムか触媒成分担持層の表面から厚さ方
向に、この触媒成分担持層の厚さの0%より大きく80
%以下に相当する上層部分のみに含有されている。The catalyst of the present invention has a catalyst component containing the components (a) to (c) listed above supported on the above-mentioned refractory three-dimensional structure, and has a thickness of 80% or less of the thickness of the catalyst component supporting layer. It is characterized in that rhodium is contained only in the layer portion with a thickness corresponding to 0% (excluding 0% where no rhodium is present). That is, in the catalyst of the present invention, rhodium is larger than 80% of the thickness of the catalyst component support layer in the thickness direction from the surface of the catalyst component support layer.
% or less is contained only in the upper layer portion.
上記のようにロジウムを触媒成分担持層の上層部分のみ
に含有させる方法については特に制限はなく、−例とし
て次のものを挙げることができる。As mentioned above, there is no particular restriction on the method of containing rhodium only in the upper layer of the catalyst component supporting layer, and examples include the following.
すなわち、耐火性無機酸化物(a)および白金および/
またはパラジウム(1))を含有する触媒成分を耐火性
三次元構造体上に担持して第1層を形成し、次いて耐火
性無機酸化物(a)およびロジウム(c)を含有する触
媒成分をに記第1層」−に担持して第2層を形成し、こ
れにより上層部分としての第2層のみにITラジウムC
)が含有された触媒成分担持層か形成される。That is, refractory inorganic oxide (a) and platinum and/or
Alternatively, a catalyst component containing palladium (1) is supported on a refractory three-dimensional structure to form a first layer, and then a catalyst component containing a refractory inorganic oxide (a) and rhodium (c) is formed. The second layer is formed by supporting IT radium C on the first layer.
) is formed.
」二記第2層にざらに白金および/またはバラシラノ、
(b)を含有させることもてきるか、第1層に白金およ
び/またはパラジウム(b)を、第2層にロジウム(c
)を選択的に含有させるほうが貴金属の使用形態として
は最も効果的である。” 2. In the second layer, platinum and/or rose silano,
Platinum and/or palladium (b) may be included in the first layer and rhodium (c) in the second layer.
) is the most effective way to use precious metals.
本発明の触媒は、上記耐火性無n酸化物(a)、白金お
よび/またはパラジウム(1))およびロジウム(c)
のほか!こ、ランタン、セリウム、プラセオジム、ネオ
ジム、1ノマリウムなどの希土類元素から選ばれる少な
くとも1種の元素を含有していてもよい。The catalyst of the present invention comprises the above refractory n-free oxide (a), platinum and/or palladium (1)) and rhodium (c).
Besides! It may contain at least one element selected from rare earth elements such as lanthanum, cerium, praseodymium, neodymium, and monomarium.
本発明の触媒において、触媒成分担持層な構成する耐火
性無機酸化物(a)、白金および/また(よパラジウム
(1))、およびロジウム(c)の担持量は、耐火性三
次元構造体1g当りそれぞれ3〜300g、0より太き
く6g以下、0より太きく3g以下、および0.01〜
1gの範囲にあるのか好ましい。In the catalyst of the present invention, the amount of the refractory inorganic oxide (a), platinum and/or palladium (1), and rhodium (c) constituting the catalyst component support layer is determined by the amount of the refractory three-dimensional structure. 3 to 300g per 1g, thicker than 0 and 6g or less, thicker than 0 and 3g or less, and 0.01 to
It is preferable that the amount is in the range of 1 g.
なお、必要に応じて添加する上記希土類元素のノリ持量
は、耐火性三次元構造体1g当り1〜5゜gの範囲にあ
るのが好ましい。The amount of the rare earth element added as necessary is preferably in the range of 1 to 5 g per 1 g of the refractory three-dimensional structure.
前記のとおり、本発明の触媒においてシL、ロジウム(
c)か必須成分として含有され、しかもこのロジウム(
c)を含有する上層部分が全触媒成分担持層の厚さの少
なくとも80%を占めることが必要であり、ロジウム(
c)か含まれていないか、またにを含まれていたにして
も、それを含有する上層部分か全触媒成分担1..j層
の厚さの80%を超えると微粒子物質の除去能か低下し
て本発明の目的を達成することかできない。As mentioned above, in the catalyst of the present invention, SiL, Rhodium (
c) is contained as an essential component, and this rhodium (
c) It is necessary that the upper layer portion containing rhodium (
c) or not, or even if it does, the upper layer containing it or the entire catalyst component carrier 1. .. If the thickness exceeds 80% of the thickness of layer j, the ability to remove particulate matter will decrease, making it impossible to achieve the object of the present invention.
本発明の触媒の調製方法については、特に制限はなく、
具体例を挙げれは次のとおりである。There are no particular restrictions on the method for preparing the catalyst of the present invention.
Specific examples are as follows.
(1) 耐火性無機酸化物の粉体を湿式粉砕してスラリ
ー化し、このスラリーに耐火性三次元構造体を浸漬し、
余分なスラリーを取り除いた後、80〜250°Cで乾
燥し、次いて300〜850°Cて夕尭成する。(1) A refractory inorganic oxide powder is wet-pulverized into a slurry, a refractory three-dimensional structure is immersed in this slurry,
After removing excess slurry, it is dried at 80-250°C, and then heated at 300-850°C.
次に、上記耐火性三次元構造体を所定f(’zの「Iシ
ウム化合物を含有する水溶液中に浸漬し、ロジウム化合
物を吸着担持した後、余分な溶液を取り除き、80〜2
50°Cて乾燥し、次いて300〜850°Cて焼成す
る。Next, the above refractory three-dimensional structure is immersed in an aqueous solution containing a sium compound of a predetermined f('z) to adsorb and support the rhodium compound, and then the excess solution is removed and the 80-2
Dry at 50°C and then bake at 300-850°C.
最後に、上記耐火性三次元構造体を白金および/または
パラジウムの化合物の所定量を含有する水溶液中に浸漬
−余分なM i’fりを取り除いた後、80〜250°
Cで乾燥し、次いて300〜850°Cて焼成して目的
とする触媒を得る。Finally, the refractory three-dimensional structure is immersed in an aqueous solution containing a predetermined amount of platinum and/or palladium compounds - after removing excess M i'f
The catalyst is dried at C and then calcined at 300 to 850 C to obtain the desired catalyst.
(2) 1Tli’l火性三次元構造体を、白金およ
び/またはパラジウムの化合物と耐火性無機酸化物とを
含有するスラリー中に浸漬し、余分なスラリーを取り除
いた後、80〜250°Cで+2燥し、次いて300〜
800°Cて焼成して第1層を形成する。(2) The 1Tli'l refractory three-dimensional structure is immersed in a slurry containing a platinum and/or palladium compound and a refractory inorganic oxide, and after removing excess slurry, the temperature is 80 to 250°C. +2 drying, then 300~
The first layer is formed by firing at 800°C.
次に、」−記第1層を形成した耐火性三次元構造体をロ
ジウム化合物と耐火性11I+′機酸化物とを含有する
スラリー中に浸漬し、余分なスラリーを取り除いた後、
80〜250℃で乾燥し、次いて300〜800°Cて
焼成して第2層を形成して、目的とする触媒を得る。Next, the refractory three-dimensional structure with the first layer formed thereon is immersed in a slurry containing a rhodium compound and a refractory 11I+' organic oxide, and after removing excess slurry,
It is dried at 80-250°C and then calcined at 300-800°C to form a second layer to obtain the desired catalyst.
(発明の効果)
本発明の触媒jよ、炭素系微粒子のほか未燃焼炭化水素
、−・酸化炭素なとの有害成分の低温からの燃頬除去性
能に優れ、しかも二酸化硫黄の酸化能か低いことからザ
ルフエー)・の生成を抑制することができる。従って、
本発明の触媒は、ディーゼルエンジン排ガス中の微粒子
物質の低減化に優れ、本発明の触媒を使用することによ
りディーゼルエンジン排ガスを効率よく浄化することか
できる。(Effects of the Invention) The catalyst of the present invention has excellent performance in removing harmful components such as carbon-based fine particles, unburned hydrocarbons, and carbon oxides from low temperatures, and has a low ability to oxidize sulfur dioxide. Therefore, it is possible to suppress the production of Zarphae). Therefore,
The catalyst of the present invention is excellent in reducing particulate matter in diesel engine exhaust gas, and by using the catalyst of the present invention, diesel engine exhaust gas can be efficiently purified.
本発明の触媒は、SOFの除去能ごこおいても優れてい
ることから、ディーゼルエンジン排ガスの浄化にきわめ
て効果的である。Since the catalyst of the present invention has excellent SOF removal ability, it is extremely effective in purifying diesel engine exhaust gas.
ざらに、本発明の触媒は、高温面l久性にも優れている
ことから実用」二問題を生しることなくティーセル車に
搭載することができる。In general, the catalyst of the present invention also has excellent high-temperature surface durability, so it can be installed in a Tea Cell vehicle without causing any practical problems.
上記のように、本発明の触媒は、ディーゼルエンジン排
ガス浄化用触媒としてきわめて有用なものである。As described above, the catalyst of the present invention is extremely useful as a catalyst for purifying diesel engine exhaust gas.
(実施例)
以下、実施例を挙けて本発明をざらに具体的に説明する
。(Examples) Hereinafter, the present invention will be roughly and specifically explained with reference to Examples.
なお、触媒成分担持層におけるロジウムの分布状>y1
7こついてはEPMA(Electron Probe
Micr。In addition, the distribution shape of rhodium in the catalyst component supporting layer>y1
7 If you get stuck, use EPMA (Electron Probe).
Micr.
analyzer) (品性製作所(株)製)を用いて
測定した。analyzer) (manufactured by Kinsei Seisakusho Co., Ltd.).
実施例1
比表面積90m2/gのアルミナ1kgを、パラジウム
として12.5gを含有する硝酸パラジウム(以下、硝
酸パラジウム12.5g(パラジウム換算)のように表
記する)を脱イオン水に溶解した水溶液に投入し、十分
かきまぜた後、150°Cて3時間乾燥上 ざらに50
0℃で2時間焼成してアルミナ−パラジウム粉体をマH
た。Example 1 1 kg of alumina with a specific surface area of 90 m2/g was added to an aqueous solution in which palladium nitrate (hereinafter referred to as 12.5 g of palladium nitrate (palladium equivalent)) containing 12.5 g of palladium was dissolved in deionized water. Pour in, stir thoroughly, and dry at 150°C for 3 hours.
The alumina-palladium powder is macerated by firing at 0℃ for 2 hours.
Ta.
この粉体11(gを湿式粉砕してスラリー化した。This powder 11 (g) was wet-pulverized to form a slurry.
このスラリーに横断面1平方インチ当り約300個のオ
ーブンフIコーのガス流通セルを有する5、66インチ
径X6.OOインチ長さの円筒状のコージュライト製ハ
ニカム担体を浸漬し、余分なスラリーを取り除いた後、
150°Cで2時間乾燥し、次いて500℃で1時間焼
成して、アルミナ−パラジウム粉体を構造体1g当り8
1g担持した構造体を得た。This slurry has a 5.66 inch diameter x 6.5 mm diameter oven cell with approximately 300 oven cells per square inch of cross section. After soaking a 0 inch long cylindrical cordierite honeycomb carrier and removing the excess slurry,
The alumina-palladium powder was dried at 150°C for 2 hours and then calcined at 500°C for 1 hour to obtain a
A structure carrying 1 g was obtained.
次いで、比表面積90m、”/gのアルミナ11<gを
、硝酸ロジウム5g(ロジウム換算)を脱イオン水に溶
解した水溶液に投入し、十分かきまぜた後、150°C
て3時間乾燥し、次いて500°Cて2時間焼成してア
ルミナ−ロジウム粉体を得た。Next, 11<g of alumina with a specific surface area of 90 m/g was added to an aqueous solution containing 5 g of rhodium nitrate (rhodium equivalent) dissolved in deionized water, stirred thoroughly, and heated at 150°C.
The powder was dried at 500°C for 3 hours, and then fired at 500°C for 2 hours to obtain alumina-rhodium powder.
このアルミナ−ロジウム粉体1kgを湿式粉砕してスラ
リー化し、この上記アルミナ−パラジウム担持構造体を
浸漬し、余分なスラリーを取り除いた後、150℃で3
時間乾燥し、次いて500°Cて1時間焼成して、この
アルミナ−ロジウム粉体を構造体IQ当り20.1g担
持した触媒を得た。1 kg of this alumina-rhodium powder was wet-pulverized to form a slurry, and the above-mentioned alumina-palladium supporting structure was immersed, and after removing excess slurry, it was heated at 150°C for 30 minutes.
The catalyst was dried for an hour and then calcined at 500°C for an hour to obtain a catalyst in which 20.1 g of this alumina-rhodium powder was supported per structure IQ.
この触媒における、アルミナ、パラジウムおよびロジウ
ムの担持量は、構造体12当り100g、1gおよび0
.1 gであった。The supported amounts of alumina, palladium, and rhodium in this catalyst were 100 g, 1 g, and 0 g per structure 12.
.. It was 1g.
また、ロジウムは触媒成分担持層の厚さの30%に相当
する厚さの上層部分のみに含有されていた。Further, rhodium was contained only in the upper layer portion having a thickness corresponding to 30% of the thickness of the catalyst component supporting layer.
実施例2
比表面積150m2/gのアルミナ1kgを、ジニトロ
ジアミノ白金20g(白金換算)を脱イオン水に溶解し
た水溶液に投入し、十分かきまぜた後、150°Cて3
時間乾燥し、次いて500℃て21稍開カ°ε成してア
ルミナ−白金粉体を得た。Example 2 1 kg of alumina with a specific surface area of 150 m2/g was added to an aqueous solution in which 20 g of dinitrodiaminoplatinum (in terms of platinum) was dissolved in deionized water, stirred thoroughly, and heated at 150°C for 3 hours.
It was dried for an hour and then opened for 21 minutes at 500°C to obtain an alumina-platinum powder.
この粉体1kgを湿式粉砕してスラリー化し、このスラ
リーに実施例1て使用したと同しコージュライト製ハニ
カム担体を浸漬し、余分なスラリーを取り除いた後、1
50°Cて2時間乾燥し、次いて500°Cて1時間焼
成して、アルミナ−白金粉体を構造体1g当り51g担
持した構造体を得た。1 kg of this powder was wet-pulverized to form a slurry, and the same cordierite honeycomb carrier used in Example 1 was immersed in this slurry, and after removing excess slurry,
It was dried at 50°C for 2 hours and then fired at 500°C for 1 hour to obtain a structure in which 51 g of alumina-platinum powder was supported per 1 g of the structure.
次いて、比表面積90m2/gのアルミナIkgを、硝
酸ロジウム10g(ロジウム換算)を脱イオン水に溶解
した水溶液に投入し、十分かきまぜた後、150°Cて
3時間乾燥し、次いて500℃で2時間焼成してアルミ
ナ−ロジウム粉体を得た。Next, Ikg of alumina with a specific surface area of 90 m2/g was poured into an aqueous solution of 10 g of rhodium nitrate (rhodium equivalent) dissolved in deionized water, thoroughly stirred, dried at 150°C for 3 hours, and then heated to 500°C. The mixture was fired for 2 hours to obtain alumina-rhodium powder.
このアルミナ−ロジウム粉体1kgを湿式粉砕してスラ
リー化し、このスラリーに上記アルミナ白金担持構造体
を浸漬し、余分なスラリーを取り除いた後、150’C
て3時間乾燥し、次いて500°Cて1時間焼成して、
アルミナ−白金粉体な構遺体1Ω当り50.5 g担持
した触媒を得た。1 kg of this alumina-rhodium powder was wet-pulverized to form a slurry, the alumina platinum supporting structure was immersed in this slurry, excess slurry was removed, and the mixture was heated to 150°C.
dried for 3 hours, then baked at 500°C for 1 hour,
A catalyst was obtained in which 50.5 g of alumina-platinum powder was supported per 1Ω of the structure.
この触媒における、アルミナ、白金およびロジウムの担
持量は、構造体1g当りそれぞれ100g−1gおよび
0.5gであった。The supported amounts of alumina, platinum, and rhodium in this catalyst were 100 g-1 g and 0.5 g, respectively, per 1 g of the structure.
また、ロジウムは触媒成分担持層の厚さの60%に相当
する厚さの北層部分のみに含有されていた。Further, rhodium was contained only in the northern layer portion whose thickness corresponded to 60% of the thickness of the catalyst component supporting layer.
実施例3
比表面積150 m2/ gのアルミナ11Kgを、硝
酸パラジウム16.7g(パラジウム換算)および塩化
白金酸8.3g(白金換rF−)を脱イオン水に溶解し
た水溶液ζこ投入し、十分かきまぜた後、150°Cて
3時間乾燥し、ついて750′Cて1時間焼成してアル
ミナ−パラジウム−白金粉体を得た。Example 3 11 kg of alumina with a specific surface area of 150 m2/g was charged into an aqueous solution ζ in which 16.7 g of palladium nitrate (in terms of palladium) and 8.3 g of chloroplatinic acid (rF- in terms of platinum) were dissolved in deionized water. After stirring, the mixture was dried at 150°C for 3 hours and then calcined at 750'C for 1 hour to obtain alumina-palladium-platinum powder.
この粉体1kgを湿式粉砕してスラリー化し、このスラ
リーごこ実施例1て使用したと同しコージュライト製ハ
ニカム担体を浸漬し、余分なスラリーを取り除いた後、
150’Cて2時間乾燥腰 次いて500℃で1時間焼
成して、このアルミナパラジウム−白金粉体を構造体1
2当り62g担持した構造体を得た。1 kg of this powder was wet-pulverized into a slurry, and the same cordierite honeycomb carrier used in Example 1 was immersed in the slurry, and the excess slurry was removed.
The alumina palladium-platinum powder was dried for 2 hours at 150°C, then fired at 500°C for 1 hour.
A structure was obtained in which 62 g was supported per 2 pieces.
次いて、比表面積120 m2/ gのアルミナ1kg
を、ヘキサアンミンロジウムクロライド12.5g(ロ
ジウム換算)を脱イオン水に溶解した水溶液に投入し、
十分かきまぜた後、180 ’Cで3時間乾燥し、次い
て500℃で1時間焼成してアルミナ−ロジウム粉体を
得た。このアルミナ−ロジウム粉体1kgを湿式粉砕し
てスラリー化し、このスラリーに上記アルミナ−パラジ
ウム−白金担持構造体を浸漬し、余分なスラリーを取り
除いた後、150℃で2時間乾燥し、次いて500 ’
Cて1時間焼成して、アルミナ−ロジウム粉体を構造体
1g当り40.5g担持したM;媒をtHか。Next, 1 kg of alumina with a specific surface area of 120 m2/g
was added to an aqueous solution of 12.5 g (rhodium equivalent) of hexaammine rhodium chloride dissolved in deionized water,
After thorough stirring, the mixture was dried at 180'C for 3 hours, and then calcined at 500C for 1 hour to obtain alumina-rhodium powder. 1 kg of this alumina-rhodium powder was wet-pulverized to form a slurry, and the above-mentioned alumina-palladium-platinum supporting structure was immersed in this slurry, and after removing excess slurry, it was dried at 150°C for 2 hours, and then '
The structure was calcined for 1 hour at C and tH to support 40.5 g of alumina-rhodium powder per 1 g of the structure.
この触媒における、アルミナ、パラジウム、白金および
ロジウムの担持量は、構造体1g当りそれぞれ100g
、1g、0,5gおよび0.5gてあフた。The amount of alumina, palladium, platinum and rhodium supported in this catalyst is 100g each per 1g of structure.
, 1g, 0.5g and 0.5g tea.
また、ロジウムは触媒成分担持層の厚さの50%に相当
する厚さの」−層部分のみに含有されてぃ実施例4
比表面積80m2/gのジルコニアIkgを、硝酸パラ
ジウム20g(パラジウム換算)を脱イオン水に溶解し
た水溶液に投入し、十分かきまぜた後、150℃で6時
間乾燥し、次いて700°Cて1時間焼成してジルコニ
ア−パラジウム粉体を得た。In addition, rhodium is contained only in the layer portion with a thickness corresponding to 50% of the thickness of the catalyst component supporting layer. was added to an aqueous solution of deionized water, thoroughly stirred, dried at 150°C for 6 hours, and then calcined at 700°C for 1 hour to obtain zirconia-palladium powder.
この粉体1kgを湿式粉砕してスラリー化し、このスラ
リーを実施例1で使用したと同じコーシュライト製ハニ
カム担体に浸漬し、余分なスラリーを取り除いた後、1
50℃で3時間乾燥し、吹いて500°Cて1時間焼成
して、ジルコニア−パラジウム粉体を構造体12当り5
1g担持した構造体を得た。1 kg of this powder was wet-pulverized to form a slurry, and this slurry was immersed in the same caushlite honeycomb carrier used in Example 1. After removing excess slurry,
The zirconia-palladium powder was dried at 50°C for 3 hours, blown and fired at 500°C for 1 hour to form a powder of zirconia-palladium powder of 50% per 12 structures.
A structure carrying 1 g was obtained.
次いて、比表面積80rn2/gのジルコニアIJ<
gを、硝酸ロジウム20g(ロジウム換算)を脱イオン
水に溶解した水溶液に投入し、十分かきまぜた後、15
0°Cで3時間乾燥し、次いて500°Cで1時間焼成
してジルコニア−ロジウム粉体をj8た。Next, zirconia IJ with a specific surface area of 80rn2/g<
g was added to an aqueous solution of 20 g of rhodium nitrate (rhodium equivalent) dissolved in deionized water, and after stirring thoroughly,
It was dried at 0°C for 3 hours and then fired at 500°C for 1 hour to obtain a zirconia-rhodium powder.
このジルコニア−ロジウム粉体を湿式粉砕してスラリー
化し、このスラリーに上記ジルコニア−パラジウム担持
構造体を浸漬し、余分なスラリーを取り除いた後、18
0℃で2時間乾燥し、次いて700°Cて2時間焼成し
て、ジルコニア−ロジウム粉体を構造体1g当り5.1
g担持した触媒を得た。This zirconia-rhodium powder was wet-pulverized to form a slurry, and the zirconia-palladium supporting structure was immersed in this slurry, and after removing excess slurry,
The zirconia-rhodium powder was dried at 0°C for 2 hours and then fired at 700°C for 2 hours to obtain a powder of zirconia-rhodium powder of 5.1
A supported catalyst was obtained.
この触媒におげろ、ジルコニア、パラジウムおよびロジ
ウムの担持量は構造体12当りそれぞれ55g、Igお
よび0,1gであった。The amounts of zirconia, palladium and rhodium supported on this catalyst were 55 g, Ig and 0.1 g, respectively, per 12 structures.
また、ロジウムは触媒成分担持層の厚さの20%に相当
する厚さの上層部分のみに含有されていた。Further, rhodium was contained only in the upper layer portion having a thickness corresponding to 20% of the thickness of the catalyst component supporting layer.
実施例5
比表面積60m2/gのジルコニア11(gを、塩化パ
ラジウム25g(パラジウム換算)および硝酸プラセオ
ジム165gを脱イオン水に溶解した水溶液に投入腰
十分かきまぜた後、150’Cて6時間乾燥腰次いて5
00 ’Cで2時間焼成してアルミナ−パラジウム−酸
化プラセオジム粉体を得た。Example 5 Zirconia 11 (g) with a specific surface area of 60 m2/g was poured into an aqueous solution in which 25 g of palladium chloride (palladium equivalent) and 165 g of praseodymium nitrate were dissolved in deionized water.
After stirring thoroughly, dry at 150'C for 6 hours.
The powder was calcined at 00'C for 2 hours to obtain alumina-palladium-praseodymium oxide powder.
この粉体1kgを湿式粉砕してスラリー化し、このスラ
リーに横断面1平方インチ当り約300個のオープンフ
ローのガス流通セルを有する5゜66インチ径×6.0
インチ長さの円筒状のステンレス製ハニカム担体を浸漬
し、余分なスラリーを取り除いた後、180°Cで2時
間乾燥し、次いて650℃で3時間焼成してアルミナ−
パラジウム−酸化プラセオジム粉体を構造体1g当り8
7g担持した構造体を得た。1 kg of this powder is wet-milled into a slurry, and this slurry is made into a 5° 66 inch diameter x 6.
After soaking an inch-long cylindrical stainless steel honeycomb carrier and removing excess slurry, it was dried at 180°C for 2 hours, and then calcined at 650°C for 3 hours to remove the alumina.
Palladium-praseodymium oxide powder per gram of structure
A structure carrying 7g was obtained.
次いて、比表面積90m2/gのジルコニア1kgを、
硝酸ロジウム5g(ロジウム換算)を脱イオン水に溶解
した水溶液に投入し、十分かきまぜた後、1508Cで
3時間乾燥し、次いて500°Cて2時間焼成してシル
コニアーロシウJ1粉体な得た。Next, 1 kg of zirconia with a specific surface area of 90 m2/g,
5 g of rhodium nitrate (rhodium equivalent) was added to an aqueous solution of deionized water, thoroughly stirred, dried at 1508 C for 3 hours, and then calcined at 500 C for 2 hours to obtain Silconia Rhosi J1 powder. Ta.
この粉体1kgを湿式粉砕してスラリー化し、このスラ
リーに上記パラシ1クムー酸化プラセオジム担持構造体
を浸漬し、余分なスラリーを取り除いた後、]、 50
’Cて6時間乾燥し、次いて400°Cて1時間焼成
して、ジルコニア−ロジウム粉体を構造体12当り20
.1g担持した触媒を得た。1 kg of this powder was wet-pulverized to form a slurry, the above parasicum praseodymium oxide supporting structure was immersed in the slurry, and the excess slurry was removed.], 50
The zirconia-rhodium powder was dried at 400°C for 6 hours and then fired at 400°C for 1 hour to form a zirconia-rhodium powder of 20
.. 1g of supported catalyst was obtained.
この触媒におりる、ジルコニア、パラジウム、ロジウム
および酸化プラセオジムの担持量は、構造体1g当りそ
れぞれ100g、2g、0.1gおよび5gてあフた。The supported amounts of zirconia, palladium, rhodium, and praseodymium oxide in this catalyst were 100 g, 2 g, 0.1 g, and 5 g, respectively, per 1 g of the structure.
また、ロジウムは触媒成分担持層の厚さの30%に相当
する厚さの上層部分のみに含有されていた。Further, rhodium was contained only in the upper layer portion having a thickness corresponding to 30% of the thickness of the catalyst component supporting layer.
実施例6
比表面積150m”/gのアルミナIkgを、ジニトロ
ジアミノ白金20g(白金換算)および硝酸セリウム1
510gを脱イオン水に溶解した水溶液に投入し、十分
かきまぜた後、150℃で6時間乾燥し、次いて500
℃で2時間焼成してアルミナ−白金−七リア粉体を得た
。Example 6 I kg of alumina with a specific surface area of 150 m"/g was mixed with 20 g of dinitrodiaminoplatinum (in terms of platinum) and 1 kg of cerium nitrate.
510g was added to an aqueous solution dissolved in deionized water, thoroughly stirred, and then dried at 150°C for 6 hours.
It was calcined for 2 hours at ℃ to obtain an alumina-platinum-sevenia powder.
この粉体1kgを湿式粉砕してスラリー化し、このスラ
リーに横断面1平方インチ当り約200個のオープンフ
ローのガス流通セルを有する5゜66インチ径X6.0
0インチ長さの円筒状のコーシエライ]・製ハニカム担
体を浸漬腰余分なスラリーを取り除いた後、150°C
て3時間乾燥し、次いて400℃で2時間焼成してアル
ミナ−は金セリア粉体を構造体IQ当り81g担持した
構造体を得た。1 kg of this powder is wet-milled to form a slurry, and this slurry is made into a 5° 66 inch diameter x 6.
A cylindrical honeycomb carrier of 0 inch length was soaked at 150°C after removing excess slurry.
The structure was then dried at 400 DEG C. for 2 hours to obtain a structure in which 81 g of alumina and gold ceria powder was supported per structure IQ.
次いで、比表面積150m2/gのアルミナ1kgを、
硝酸ロジウム5g(ロジウム換算)および硝酸ランタン
266gを脱イオン水に溶解した水溶液に投入し、十分
かきまぜた後、150°Cて3時間乾燥し、次いて50
0°Cて1時間焼成してアルミナ−〇ジウムー酸化ラン
タン粉体を得た。Next, 1 kg of alumina with a specific surface area of 150 m2/g,
5 g of rhodium nitrate (rhodium equivalent) and 266 g of lanthanum nitrate were dissolved in deionized water, stirred thoroughly, and then dried at 150°C for 3 hours.
The mixture was fired at 0°C for 1 hour to obtain alumina-〇dium-lanthanum oxide powder.
この扮K l k gを湿式粉砕してスラリー化し、こ
のスラリーに上記アルミナ−白金−七リア担持構造体を
浸漬し、余分なスラリーを取り除いた後、150°Cて
3時間乾燥し、次いて600°Cて1時間焼成してアル
ミナ−ロジウム−酸化ランタン粉体を構造体IQ当り1
10.5g担持した触媒を得た。This Klkg was wet-pulverized to form a slurry, and the alumina-platinum-septalia support structure was immersed in this slurry, excess slurry was removed, and then dried at 150°C for 3 hours. After firing at 600°C for 1 hour, the alumina-rhodium-lanthanum oxide powder was produced at 1 per structure IQ.
10.5g of supported catalyst was obtained.
この触媒において、アルミナ、白金、ロジウム、セリア
および酸化ランタンの担持量は、構造体12当りそれぞ
れ150g、1g、0.5g、30gおよび10gであ
った。In this catalyst, the supported amounts of alumina, platinum, rhodium, ceria, and lanthanum oxide were 150 g, 1 g, 0.5 g, 30 g, and 10 g per structure 12, respectively.
また、ロジウムは触媒成分担持層の厚さの70%に相当
する厚さの上層部分のみに含有されていた。Further, rhodium was contained only in the upper layer portion, which corresponded to 70% of the thickness of the catalyst component supporting layer.
実施例7
比表面積55m2/gのシリカ1kgを、塩化パラジウ
ム20g(パラジウム換算)および塩化白金酸6g(白
金換算)を脱イオン水に溶解した水溶液に投入し、十分
かきまぜた後、150°Cて3時間乾燥上 次いて60
0°Cて2時間焼成してシリカ−パラジウム−白金粉体
を得た。Example 7 1 kg of silica with a specific surface area of 55 m2/g was added to an aqueous solution in which 20 g of palladium chloride (in terms of palladium) and 6 g of chloroplatinic acid (in terms of platinum) were dissolved in deionized water, stirred thoroughly, and then heated at 150°C. Dry for 3 hours, then 60
The mixture was calcined at 0°C for 2 hours to obtain silica-palladium-platinum powder.
この粉体1kgを湿式粉砕してスラリーイヒし、このス
ラリーに実施例5て使用したと同じステンレス製ハニカ
ム担体を浸漬し、余分なスラリーを取り除いた後、15
0°Cて3時間乾燥し、次いて500℃で1時間焼成し
て、シリカ−パラジウム白金粉体を構造体1g当り51
.3担持した構造体を得た。1 kg of this powder was wet-pulverized to form a slurry, and the same stainless steel honeycomb carrier as used in Example 5 was immersed in this slurry, and after removing excess slurry,
The silica-palladium platinum powder was dried at 0°C for 3 hours and then calcined at 500°C for 1 hour to obtain a
.. A structure carrying 3 was obtained.
次いて、比表面積65rn2/gのチタニア11りgを
、硝酸ロジウム50g(ロジウム換算)を脱イオン水に
溶解した水溶液に投入し、十分かきまぜた後、150°
Cて3時間乾燥し 次いて400°Cで1時間焼成して
チタニア−ロジウム粉体を14だ。Next, 11 g of titania with a specific surface area of 65 rn2/g was added to an aqueous solution containing 50 g of rhodium nitrate (rhodium equivalent) dissolved in deionized water, stirred thoroughly, and heated to 150°
The titania-rhodium powder was dried at 400°C for 3 hours and then fired at 400°C for 1 hour.
この粉体11(gを湿式粉砕してスラリー化し、このス
ラリーに上層シリカーパラジウムー白金担持構造体を浸
漬し、余分なスラリーを取り除いた後、1500Cで3
時間乾燥上次いて500°Cて1時間焼成してナタニア
ーロシウム粉体を構造体1g当り10.5g担持した触
媒を得た。This powder 11 (g) was wet-pulverized to form a slurry, the upper layer silica palladium-platinum supporting structure was immersed in this slurry, and the excess slurry was removed.
After drying for a period of time, the structure was then calcined at 500° C. for 1 hour to obtain a catalyst in which 10.5 g of natania arosium powder was supported per 1 g of the structure.
この触媒における、シリカ、チタニア、パラジウム、白
金およびロジウムの担持量は、構造体12当りそれぞれ
50g、10g、Ig、0.3gおよび0.5gであっ
た。The supported amounts of silica, titania, palladium, platinum, and rhodium in this catalyst were 50 g, 10 g, Ig, 0.3 g, and 0.5 g per 12 structures, respectively.
また、ロジウムは触媒成分担持層の厚さの25%に相当
する厚さの上層部分のみに含有されていた。Further, rhodium was contained only in the upper layer portion having a thickness corresponding to 25% of the thickness of the catalyst component supporting layer.
実施例8
比表面積150m2/gのアルミナ1kgを、バラシウ
ムスルフイト錯塩25g(パラジウム換算)および白金
スルフィI・錯塩12.5g(白金換算)を脱イオン水
に溶解した水溶液に投入し、十分かきませた後、150
°Cて3時間乾燥上 次いて800°Cて5時間焼成し
てアルミナ−パラジウム−白金粉体を得た。Example 8 1 kg of alumina with a specific surface area of 150 m2/g was poured into an aqueous solution in which 25 g of baracium sulfite complex salt (in terms of palladium) and 12.5 g of platinum sulfite complex salt (in terms of platinum) were dissolved in deionized water. After stirring, 150
It was dried at 800°C for 3 hours and then fired at 800°C for 5 hours to obtain alumina-palladium-platinum powder.
この粉体11(gを湿式粉砕してスラリー化し、このス
ラリーに実施例1て使用したと同しコーシエライI−製
ハニカ11担体を浸漬し、余分なスラリーを取り除いた
後、150’Cて6時間乾燥し、次いて500℃で1時
間焼成してアルミナ−パラジウム−白金粉体を構造体1
g当り4.1.5g担持した構造体を得た。This powder 11 (g) was wet-pulverized to form a slurry, and the same Kosierai I-made Honey 11 carrier used in Example 1 was immersed in the slurry, and after removing the excess slurry, the mixture was heated at 150°C for 6 hours. Structure 1
A structure carrying 4.1.5 g/g was obtained.
次いて、比表面積40m2/gのジルコニア1kgを、
ジニトロジアミ、)白金8.3g(白金1象算)および
硝酸ロジウム8.3g(ロジウム換算)を脱イオン水に
溶解した水溶液ζこ投入し、十分かきJ5せた後、15
0°Cて6時間乾燥し、次いて750°Cて4時間焼成
して、ジルコニア−白金−ロジム粉体を得た。Next, 1 kg of zirconia with a specific surface area of 40 m2/g,
dinitrodiamycin,) 8.3 g of platinum (1 quadrant of platinum) and 8.3 g of rhodium nitrate (converted to rhodium) were dissolved in deionized water.
It was dried at 0°C for 6 hours and then fired at 750°C for 4 hours to obtain zirconia-platinum-rhodium powder.
この粉体11(gを湿式粉砕してスラリー化し、このス
ラリーに上記アルミナ−パラジウム−白金担持構造体を
浸漬し、余分なスラリーを取り除いた後、150℃で3
時間乾燥し、次いて400°Cて2時間焼成してジルコ
ニア−パラジウム−白金粉体を構造体1g当り61.0
g担持した触媒を得た。This powder 11 (g) was wet-pulverized to form a slurry, the alumina-palladium-platinum supporting structure was immersed in this slurry, excess slurry was removed, and the mixture was heated at 150°C for 30 minutes.
The zirconia-palladium-platinum powder was dried for 2 hours at 400°C and then baked at 400°C for 61.0 hours per gram of the structure.
A supported catalyst was obtained.
この触媒における、アルミナ、ジルコニア、パラジウム
、白金およびロシウJ1の担持量は構造体1!II当り
それぞれ40g、60g、Ig、Igおよび0.5gで
あった。The amount of alumina, zirconia, palladium, platinum, and Rossiu J1 supported in this catalyst is 1! 40g, 60g, Ig, Ig and 0.5g per II, respectively.
また、ロジウムは触媒成分担持層の厚さの70%に相当
する厚さの上層部分のみに含有されていた。Further, rhodium was contained only in the upper layer portion, which corresponded to 70% of the thickness of the catalyst component supporting layer.
実施例9
比表面積150m2/gのアルミナ1kgを秤取り、水
と湿式粉砕してスラリー化した。このスラリーに横断面
1平方インチ当り約400個のオープンフローのガス流
通セルを有する5、66インチ径X6.OOインチ長さ
の円筒状コージェライト製ハニカム担体を浸漬し、余分
なスラリーを取り除いた後、150℃で3時間乾燥し、
次いて500°Cて1時間焼成してアルミナを担持した
構造体を得た。Example 9 1 kg of alumina having a specific surface area of 150 m2/g was weighed and wet-pulverized with water to form a slurry. This slurry has a 5.66 inch diameter x 6.5 mm diameter with approximately 400 open flow gas flow cells per square inch of cross section. A cylindrical cordierite honeycomb carrier with a length of OO inches was immersed, excess slurry was removed, and then dried at 150°C for 3 hours.
Next, it was fired at 500°C for 1 hour to obtain a structure supporting alumina.
この構造体を、ロジウムとして0.4g含有する80°
Cの硝酸ロジウム水溶液2,5Qに浸漬し、ロジウムを
吸着させ、余分な溶液を取り除いた後、150℃で3時
間乾燥し、ついて700℃で1時間焼成してロジウムを
上記アルミナ担持構造体上に担持させた。This structure is 80° containing 0.4g of rhodium.
It was immersed in a rhodium nitrate aqueous solution 2.5Q of C to adsorb rhodium, and after removing the excess solution, it was dried at 150°C for 3 hours, and then calcined at 700°C for 1 hour to transfer rhodium onto the alumina support structure. It was carried by
次いて、塩仕臼金酸3.8g(白金換算)および塩化パ
ラジウム38.5g(パラジウム換算)を脱イオン水ζ
こ溶解した水溶液2.59に上層アルミナーロジウム担
持構造体を浸漬し、余分な溶液を取り除いた後、150
°Cて3時間乾燥し、次いて500°Cて2時間焼成し
て触媒を得た。Next, 3.8 g of salt-milled auric acid (in terms of platinum) and 38.5 g of palladium chloride (in terms of palladium) were added to deionized water ζ
The upper layer alumina rhodium supporting structure was immersed in an aqueous solution containing 2.5% of this solution, and after removing excess solution, 150% of the aqueous solution was dissolved.
The catalyst was dried at 500°C for 3 hours and then calcined at 500°C for 2 hours.
この触媒における、アルミナ、パラジウム、白金および
ロジウムの担持量は、構造体1g当り50g、2g、0
.2gおよび0.2gであった。The supported amounts of alumina, palladium, platinum, and rhodium in this catalyst are 50 g, 2 g, and 0 g per 1 g of the structure.
.. 2g and 0.2g.
また、ロジウムは触媒成分担持層の厚さの20%に相当
する厚さの上層部分のみに含有されていた。Further, rhodium was contained only in the upper layer portion having a thickness corresponding to 20% of the thickness of the catalyst component supporting layer.
実施例10
セラミックの骨格で形成される気泡の数か1インチ間に
約12個であるセル数を有し、空孔率か約90%である
5、66インチ径X 6 、00インチ長さの円筒状の
コージェライト製セラミックフオームを用いた以外乙よ
実施例4と同様にして触媒を得た。Example 10 Ceramic skeleton formed with a cell count of about 12 per inch and a porosity of about 90% 5.66 inch diameter x 6.00 inch length A catalyst was obtained in the same manner as in Example 4, except that a cylindrical cordierite ceramic foam was used.
この触媒における、ジルコニア、パラジウムおよびロジ
ウムの担持量は、構造体Ig当りそれぞれ55g、1g
および0.1 gであった。The supported amounts of zirconia, palladium, and rhodium in this catalyst are 55 g and 1 g, respectively, per Ig of structure.
and 0.1 g.
また、ロジウムは触媒成分担持層の厚さの20%に相当
する厚さの上層部分のみに含有されていた。Further, rhodium was contained only in the upper layer portion having a thickness corresponding to 20% of the thickness of the catalyst component supporting layer.
比較例1
比表面積150m2/gのアルミナIkgを、硝酸パラ
ジウム10g(パラジウム換算)を脱イオン水に溶解し
た水溶液に投入し、十分かきまぜた後、150℃で3時
間乾燥し、次いて500″C31、−
て1時間焼成してアルミナ−パラジウム粉体を得た。Comparative Example 1 Ikg of alumina with a specific surface area of 150 m2/g was poured into an aqueous solution in which 10 g of palladium nitrate (in terms of palladium) was dissolved in deionized water, stirred thoroughly, and dried at 150°C for 3 hours. , - and calcined for 1 hour to obtain alumina-palladium powder.
この粉体1kgを湿式粉砕してスラリー化上このスラリ
ーに実施例1で使用したと同しコージエライ(・製ハニ
カム担体を浸漬し、余分なスラリーを取り除いた後、1
50°Cて3詩間乾燥し、次いて500 ’Cて1時間
焼成して触媒を得た。1 kg of this powder was wet-pulverized to form a slurry. A honeycomb carrier manufactured by Corzierai (.
The catalyst was dried at 50°C for 3 hours and then calcined at 500°C for 1 hour.
この触媒における、アルミナおよびパラジウムの担持量
は、構造体Ig当りそれぞれ100gおよび1gであっ
た。The amounts of alumina and palladium supported in this catalyst were 100 g and 1 g, respectively, per Ig of structure.
比較例2
比較例1において、硝酸パラジウムの代わりにジニトロ
アミノ白金を用いた以外は比較例1と同様しこして触媒
を得た。Comparative Example 2 A catalyst was obtained in the same manner as in Comparative Example 1 except that dinitroaminoplatinum was used instead of palladium nitrate.
この触媒における、アルミナおよび白金の担持量は、構
造体1g当りそれぞれ100gおよび1gであった。The supported amounts of alumina and platinum in this catalyst were 100 g and 1 g, respectively, per 1 g of the structure.
比較例3
比表面積J50rrr2/gのアルミナ1kgを、硝酸
パラジウム10g(パラジウム換算)および塩化白金酸
10g(白金換算)を脱イオン水に溶解した水溶液に投
入し、十分かきまぜた後、150℃で3時間乾燥し、次
いて750℃で1時間焼成してアルミナ−パラジウム−
白金粉体を得た。Comparative Example 3 1 kg of alumina with a specific surface area J50rrr2/g was added to an aqueous solution in which 10 g of palladium nitrate (palladium equivalent) and chloroplatinic acid 10 g (platinum equivalent) were dissolved in deionized water, stirred thoroughly, and heated to 150°C for 30 minutes. The alumina-palladium-
A platinum powder was obtained.
以下、比較例1と同様にして触媒を得た。Thereafter, a catalyst was obtained in the same manner as in Comparative Example 1.
この触媒における、アルミナ、パラジウムおよび白金の
担持量は、構造体Ig当りそれぞれ100、g、Igお
よび1gであった。The supported amounts of alumina, palladium, and platinum in this catalyst were 100 g, Ig, and 1 g, respectively, per Ig of the structure.
比較例4
比表面積90m2/gのアルミナIkgを、硝酸パラジ
ウム10g(パラジウム換算)および硝酸ロジウム0.
1 g (tffジウム換算)を脱イオン水に溶解した
水溶液に投入し、十分かきまぜた後、150°Cで3時
間乾燥し、次いで500°Cて2時間焼成してアルミナ
−パラジウム−ロジウム粉体を得た。Comparative Example 4 I kg of alumina with a specific surface area of 90 m2/g was mixed with 10 g of palladium nitrate (palladium equivalent) and 0.0 g of rhodium nitrate.
1 g (TFF dium equivalent) was added to an aqueous solution dissolved in deionized water, thoroughly stirred, dried at 150°C for 3 hours, and then calcined at 500°C for 2 hours to form alumina-palladium-rhodium powder. I got it.
以下、比較例1と同様にして触媒を得た。Thereafter, a catalyst was obtained in the same manner as in Comparative Example 1.
この触媒における、アルミナ、パラジウムおよびロジウ
ムの担持量は、構造体1g当りそれぞれ100g、Ig
および0.1gであった。The supported amounts of alumina, palladium, and rhodium in this catalyst are 100 g each per 1 g of the structure, and Ig
and 0.1 g.
比較例5
比表面積150 m2/ gのアルミナ1kgを、ジニ
トロジアミノ白金10g(白金換算)および硝酸ロジウ
ム5g(ロジウム換算)を脱イオン水に溶解した水溶液
に投入し、十分かきまぜた後、150℃で3時間乾燥し
、次いて500℃で1時間焼成してアルミナ−白金−ロ
ジウム粉体を得た。Comparative Example 5 1 kg of alumina with a specific surface area of 150 m2/g was added to an aqueous solution containing 10 g of dinitrodiaminoplatinum (in terms of platinum) and 5 g of rhodium nitrate (in terms of rhodium) dissolved in deionized water, stirred thoroughly, and then heated at 150°C. It was dried for 3 hours and then calcined at 500°C for 1 hour to obtain alumina-platinum-rhodium powder.
以下、比較例1と同様にして触媒を得た。Thereafter, a catalyst was obtained in the same manner as in Comparative Example 1.
この触媒における、アルミナ、白金およびロジウムの担
持量は構造体Ig当りそれぞれ100g、1gおよび0
.5gであった。The supported amounts of alumina, platinum, and rhodium in this catalyst were 100 g, 1 g, and 0 g, respectively, per Ig of the structure.
.. It was 5g.
比較例6
比表面積150m2/gのアルミナ1kgを、硝酸パラ
ジウム10g(パラジウム換算)、塩化白金酸5g(白
金換算)およびヘギザアンミンロジウムクロライト5g
(ロジウム換算)を脱イオン水に溶解した水溶液に投入
腰 十分かきませた後、150°Cて3時間乾燥し、次
いて750℃で11侍間す尭成してアルミナ−パラジウ
ム−白金−ロジウム粉体を得た。Comparative Example 6 1 kg of alumina with a specific surface area of 150 m2/g was mixed with 10 g of palladium nitrate (in terms of palladium), 5 g of chloroplatinic acid (in terms of platinum), and 5 g of hegizaammine rhodium chlorite.
(rhodium equivalent) was added to an aqueous solution of deionized water, stirred thoroughly, and dried at 150°C for 3 hours. A powder was obtained.
以下、比較例1と同様にして触媒を得た。Thereafter, a catalyst was obtained in the same manner as in Comparative Example 1.
この触媒における、アルミナ、パラジウム、白金および
ロジウムの担持量は、構造体1g当りそれぞれ100g
、Ig、0.5gおよび0.5gであった。The amount of alumina, palladium, platinum and rhodium supported in this catalyst is 100g each per 1g of structure.
, Ig, 0.5 g and 0.5 g.
上記実施例1〜11および比較例1〜6で得られた触媒
のおける各成分の担持量、ならびにロジウムが存在する
上層部分の触媒成分担持層に対する割合をまとめて表1
に示す。 (以下余白)参考例
実施例1〜10および比較例1〜6で得られた触媒のデ
ィーゼルエンジン排ガス浄化性能を評価した。Table 1 summarizes the supported amounts of each component in the catalysts obtained in Examples 1 to 11 and Comparative Examples 1 to 6, and the ratio of the upper layer where rhodium exists to the catalyst component supported layer.
Shown below. (Left below) Reference Examples The diesel engine exhaust gas purification performance of the catalysts obtained in Examples 1 to 10 and Comparative Examples 1 to 6 was evaluated.
過給直噴式デイ−セルエンジン(4気筒、2800cc
)および燃料として硫黄含有量が0.47重量%である
軽油を用いて下記試験を行った。Supercharged direct injection day cell engine (4 cylinders, 2800cc
) and light oil with a sulfur content of 0.47% by weight as fuel.
各触媒を上層エンジンからの排ガス管に取りイ1け、エ
ンジン回転数250.Orpmの全負荷および触媒入口
温度600°Cの条件下で300時間の耐久試験を実施
した。Each catalyst is installed in the exhaust gas pipe from the upper engine, and the engine speed is 250. A 300 hour durability test was conducted under the conditions of full ORPM load and catalyst inlet temperature of 600°C.
その後、エンジン回転数2000rpm、)ルク8.5
kg−mおよび触媒入口温度300°Cの条件下で触媒
床に入る前(人口)および触媒床を出た後(出口)での
排ガス中の微粒子物質の含有量を通常のダイリューショ
ン]・ンネル法を用いて測定し、微粒子物質の除去の程
度、すなわち浄化率(%)を求めた。また、触媒床に入
る前の排ガスおよび触媒床を通過後の排ガス中の二酸化
硫黄、ガス状炭化水素および一酸化炭素の分析も同時に
行い、その転化率を求めた。After that, the engine speed is 2000 rpm,) Luk 8.5
kg-m and the catalyst inlet temperature of 300 °C, the content of particulate matter in the exhaust gas before entering the catalyst bed (population) and after leaving the catalyst bed (outlet) is determined by conventional dilution]. The degree of removal of particulate matter, that is, the purification rate (%), was determined using the tunnel method. In addition, sulfur dioxide, gaseous hydrocarbons, and carbon monoxide in the exhaust gas before entering the catalyst bed and in the exhaust gas after passing through the catalyst bed were analyzed at the same time to determine the conversion rate.
結果を表2に示す。 (以下余白)The results are shown in Table 2. (Margin below)
Claims (6)
種の貴金属、ならびに (c)ロジウムを含有する触媒成分を耐火性三次元構造
体に担持したディーゼルエンジン排ガス浄化用触媒であ
って、触媒成分担持層の厚さの80%以下に相当する厚
さの上層部分のみにロジウムが含有されていることを特
徴とするディーゼルエンジン排ガス浄化用触媒。(1) At least one selected from (a) refractory inorganic oxide, (b) palladium and platinum
A diesel engine exhaust gas purification catalyst in which a catalyst component containing various noble metals and (c) rhodium is supported on a refractory three-dimensional structure, the thickness being equivalent to 80% or less of the thickness of the catalyst component supporting layer. A diesel engine exhaust gas purification catalyst characterized by containing rhodium only in the upper layer.
造体に接する第1層が (a)耐火性無機酸化物、ならびに (b)パラジウムおよび白金から選ばれる少なくとも1
種の貴金属を含有する触媒成分からなり、また上記第1
層上の第2層が(a)耐火性無機酸化物および(c)ロ
ジウムを含有する触媒成分からなる請求項(1)に記載
のディーゼルエンジン排ガス浄化用触媒。(2) The catalyst component supporting layer consists of two layers, and the first layer in contact with the refractory three-dimensional structure is made of (a) a refractory inorganic oxide, and (b) at least one layer selected from palladium and platinum.
catalytic component containing the above-mentioned noble metal;
The catalyst for purifying diesel engine exhaust gas according to claim 1, wherein the second layer on the layer comprises a catalyst component containing (a) a refractory inorganic oxide and (c) rhodium.
ニア、ジルコニア、シリカ−アルミナ、アルミナ−ジル
コニア、アルミナ−チタニア、シリカ−チタニア、シリ
カ−ジルコニア、チタニア−ジルコニアおよびゼオライ
トよりなる群から選ばれる少なくとも1種である請求項
(1)に記載のディーゼルエンジン排ガス浄化用触媒。(3) At least the refractory inorganic oxide is selected from the group consisting of activated alumina, silica, titania, zirconia, silica-alumina, alumina-zirconia, alumina-titania, silica-titania, silica-zirconia, titania-zirconia, and zeolite. The catalyst for purifying diesel engine exhaust gas according to claim 1, which is one type of catalyst.
)に記載のディーゼルエンジン排ガス浄化用触媒。(4) Claim (1) wherein the refractory inorganic oxide is zirconia.
) The catalyst for purifying diesel engine exhaust gas described in ).
プンフローのセラミックハニカム、ウォールフロータイ
プのハニカムモノリス、オープンフローのメタルハニカ
ム、金属発泡体またはメタルメッシュである請求項(1
)に記載のディーゼルエンジン排ガス用浄化触媒。(5) Claim (1) wherein the fire-resistant three-dimensional structure is a ceramic foam, an open-flow ceramic honeycomb, a wall-flow type honeycomb monolith, an open-flow metal honeycomb, a metal foam, or a metal mesh.
) The diesel engine exhaust gas purification catalyst described in ).
クハニカムまたはオープンフローのメタルハニカムであ
る請求項(1)に記載のディーゼルエンジン排ガス用触
媒。(6) The diesel engine exhaust gas catalyst according to claim 1, wherein the refractory three-dimensional structure is an open-flow ceramic honeycomb or an open-flow metal honeycomb.
Priority Applications (6)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2159922A JP3061399B2 (en) | 1990-06-20 | 1990-06-20 | Diesel engine exhaust gas purification catalyst and purification method |
EP91110066A EP0462593B1 (en) | 1990-06-20 | 1991-06-19 | Use of a specific catalyst for purifying exhaust gases from Diesel engines |
CA002044984A CA2044984C (en) | 1990-06-20 | 1991-06-19 | Catalyst for purifying exhaust gas from diesel engines |
DE69105366T DE69105366T2 (en) | 1990-06-20 | 1991-06-19 | Use of a specific catalyst for cleaning exhaust gases from diesel engines. |
KR1019910010220A KR950010783B1 (en) | 1990-06-20 | 1991-06-19 | Use of a specific catalyst for purifying exhaust gases from disel engines |
US07/718,261 US5177041A (en) | 1990-06-20 | 1991-06-20 | Catalyst for purifying exhaust gas from diesel engines |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2159922A JP3061399B2 (en) | 1990-06-20 | 1990-06-20 | Diesel engine exhaust gas purification catalyst and purification method |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH0459049A true JPH0459049A (en) | 1992-02-25 |
JP3061399B2 JP3061399B2 (en) | 2000-07-10 |
Family
ID=15704090
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2159922A Expired - Lifetime JP3061399B2 (en) | 1990-06-20 | 1990-06-20 | Diesel engine exhaust gas purification catalyst and purification method |
Country Status (6)
Country | Link |
---|---|
US (1) | US5177041A (en) |
EP (1) | EP0462593B1 (en) |
JP (1) | JP3061399B2 (en) |
KR (1) | KR950010783B1 (en) |
CA (1) | CA2044984C (en) |
DE (1) | DE69105366T2 (en) |
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-
1990
- 1990-06-20 JP JP2159922A patent/JP3061399B2/en not_active Expired - Lifetime
-
1991
- 1991-06-19 KR KR1019910010220A patent/KR950010783B1/en not_active IP Right Cessation
- 1991-06-19 DE DE69105366T patent/DE69105366T2/en not_active Expired - Lifetime
- 1991-06-19 CA CA002044984A patent/CA2044984C/en not_active Expired - Lifetime
- 1991-06-19 EP EP91110066A patent/EP0462593B1/en not_active Expired - Lifetime
- 1991-06-20 US US07/718,261 patent/US5177041A/en not_active Expired - Lifetime
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Also Published As
Publication number | Publication date |
---|---|
DE69105366D1 (en) | 1995-01-12 |
KR950010783B1 (en) | 1995-09-23 |
CA2044984A1 (en) | 1991-12-21 |
JP3061399B2 (en) | 2000-07-10 |
EP0462593A1 (en) | 1991-12-27 |
DE69105366T2 (en) | 1995-05-18 |
US5177041A (en) | 1993-01-05 |
KR920000377A (en) | 1992-01-29 |
CA2044984C (en) | 1996-04-02 |
EP0462593B1 (en) | 1994-11-30 |
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